Research Article (Open access) |
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SSR Inst. Int. J. Life. Sci., 5(5):
2387-2392,
September 2019
Assessment
of Heavy Metals in Water of Selected Places
of Nellore coast of Andhra Pradesh through Atomic Absorption
Spectroscopy
Vardi Venkateswarlu1*,
Chenji Venkatrayulu2
1Research
Scholar, Department of Marine Biology, Vikrama Simhapuri University,
Nellore-524320, Andhra Pradesh, India
2Assistant
Professor, Department of Marine Biology, Vikrama Simhapuri University,
Nellore-524320, Andhra Pradesh, India
*Address for Correspondence: Mr. Vardi Venkateswarlu,
Research Scholar, Department of Marine Biology, Vikrama Simhapuri University,
Nellore– 524320, Andhra Pradesh, India
E-mail: venkat9160@gmail.com
ABSTRACT-
Background: The rapid industrialization of the
coastal areas has resulted in marine pollution in different regions of the
South east coast of India. The quality of coastal and marine water affected by
the toxic pollutants released from the industrial activities and urbanization
has been assessed in terms of pollution. The present study area also referred
that the industrial activity is more responsible for marine pollution, causing
toxic effects by heavy metals.
Methods:
For
the present study water samples collected from Nelaturu, Krishnapatnam coastal
villages of Nellore and samples brought to the laboratory for heavy metals
analysis by Atomic Absorption Spectroscopy (AAS) standard methods followed by
American Public Health Association (APHA).
Results:
During the present study the heavy metals Arsenic, Lead, Cadmium, Mercury,
Iron, Manganese, Copper, Zinc concentrations were observed, shown in Table 1
and discussed about the levels when compared with water quality standards given
by the Indian Standards (IS: 10500) and WHO guidelines.
Conclusion:
The present study sites are one of the famous places for marine fishing area
having near thermal power plants and port activities. In our study, there were eight heavy metals were determined, which
were observed in 2 sampling sites i.e. Nelaturu,
Krishnapatnam in Nellore district. The study had been concluded with future
impact of heavy metals in the marine environment and to the aquatic life as
well as to human life at Nellore coast.
Keywords: Atomic
Absorption Spectroscopy (AAS), Coastal water pollution, Heavy metals,
Mineralogical contamination, Nellore coast
INTRODUCTION-
Coastal
water pollution is one of the major environmental problems in the worldwide.
The coastal water pollution is due to the mineralogical contamination and
dumping of the untreated industrial and municipal wastes directly into the sea
coasts through canals. Heavy metals are generally water-soluble, no-degradable,
vigorous oxidizing agents and are strongly bonded with many biochemicals
inhibiting their functions. The rapid industrialization in coastal regions
resulted in environmental pollution and higher quantities of heavy metals are
being added into the natural estuarine and coastal environments. The heavy
metal contamination in the coastal water has connections directly to the biota
and indirectly to human life. They will also cause irregularity in blood; badly
affect the major functioning organs like kidneys and liver. Heavy metals
including both essential and nonessential elements have a particular significance
in ecotoxicology since they are highly persistent and all have the potential to
be toxic to the living organisms [1].
Heavy metals are considered the foremost
anthropogenic contaminants in coastal and marine environments worldwide [2].
They pose a serious threat to human health, natural ecosystems and living
organisms because of their toxicity, persistence and bioaccumulation
characteristics [3]. Numerous substantial heavy metals are known to
be toxic or carcinogenic to humans [4] and also play a significant
role as sensitive indicators for monitoring contaminants in aquatic systems [5].
Several studies have demonstrated that marine sediments are highly polluted by
heavy metals [6] therefore; the evaluation of metal distribution in
surface sediment is useful to assess pollution in the marine environment along
the east coast of India. Industrial activities, economic development, and
urbanization of all over the globe have risen very quickly in recent years and
substantial quantities of contaminants are introduced into rivers, estuarine
areas and coastal regions [7]. The water which provides habitats for
many aquatic organisms was polluted with various forms of hazardous and toxic
substances, including heavy metals [8]. As a result, they are considered
to be important carriers as well as the heavy metals in the aquatic cycle is
important to know the distribution and concentration of heavy metals in the
study area. In several studies, many authors investigated the distribution of
heavy metals and the pollution status using environmental assessment indices.
The
present work would be of assistance to the relevant researchers in ensuring a
heavy metals status of the neighboring coastal water bodies in Nellore, Andhra
Pradesh and would function as a foundation for further work for the present
study area. This work carried out to elucidate the coastal management by
providing primary data sets for decision-making policyholders. Also beside, the
baseline information will form a flat form for the stakeholders to monitor the
coastal pollution by inexpensive biomarkers and also manage and conserve the
study area from further pollution hazards. Further, the pollution levels for
the study area can be constantly monitored to safeguard the fishing community and
biodiversity.
MATERIALS
AND METHODS- The present study conducted during the
month of April 2019 by the Department of Marine Biology, Vikrama Simhapuri
University, Nellore, Andhra Pradesh, India.
Study Area- The
Nellore district has a 169 km of the coastal line with habitation of fishermen
community along the east coast of India. The Nellore coastal region is suitable
for the brackishwater aquaculture farming, recently gradually increased some
industrial activities. The present sampling sites of Nelaturu and Krishnapatnam
coastal areas have thermal power industries and also shipping activities from
this coastal region Fig 1.
Fig. 1: Map showing the study areas of Nelaturu
and Krishnapatnam coastal regions of Nellore coast of Andhra Pradesh in India
Sample collection- The
coastal saltwater samples were collected by following the quality sample
assortment protocol and tips given in Indian Standards strategies IS 3025
part-1 and APHA twenty-second edition. The special precautions were taken
throughout the sampling of water within the elite places of study areas. Before
the gathering of the samples, the sample containers square measure soaked night
long in a pair of aqua fortis and washed with double H2O and dried
during a clean space. At every sampling location, water samples were collected
in 2 pre-cleaned containers for duplicate mensuration. The bottles were rinsed
thrice with the coastal saltwater sample of the actual location. Total 0.5 mL
of above pure grade aqua fortis was added into the collected samples to avoid
the contamination and also to stop the loss of metals from the sample. All the
collected samples were preserved at 4oC by employing a
thermo-coal box with ice packs at the sample assortment site.
Sample
preparation for analysis- The digestion procedure for water
samples was carried out by transferring a measured volume (50 mL) of well-mixed
acid preserved water sample to a conical flask then 5 mL of concentrated nitric
acid (Conc. HNO3) was added into the flask. The water sample and
Nitric acid mixture were boiled and evaporated on a hot plate to the lowest
volume of up to 10 to 20 ml. Continued the heating and adding conc. Nitric acid
(HNO3) to the sample digestion was complete to show by a light color
clear solution in the sample digestion conical flask. After that conical flask
was washed down with distilled water and filtered. Then the filtrate was
transferred into 10 mL volumetric flask with two 5 ml of water, adding these
rinsing to the volumetric flask and cooled and diluted to the mark and mixed
thoroughly followed by Brooks et al. [9].
A portion of the sample solution was taken for required metal determinations
flowed by APHA [10].
Heavy metals analysis by
Atomic Absorption Spectroscopy- AAS
is most widely using an analytical technique for the determination of trace and
heavy metals up to parts per billion levels. AAS is a very useful technique to
determine trace levels of multi-elements in single aspiration. AA-6800 AAS
coupled with GFA-EX7 graphite furnace atomizer and ASC-6100 auto sampler from
Shimadzu (Koyoto, Japan) was used for heavy metal analysis. A high-density
graphite tube was used for atomization. Normal single hollow cathode lamps were
used for irradiation followed by APHA [10].
RESULTS- The
ranges of the heavy metals viz., Arsenic (As), Lead (Pb), Cadmium (Cd), Mercury
(Hg), Iron (Fe), Manganese (Mn), Copper (Cu) and Zinc (Zn) presented in the
coastal water of Nelaturu, Krishnapatnam regions of Nellore coast in summer
April 2019 during the study period observed the industrial activities in
thermal power station and shipping activities are more. The concentration of Pb
maximum range 4.67±0.12 was observed at Nelaturu coast, and 3.03±1.13 found at
Krishnapatnam. Cd maximum range 3.03±1.13 was observed at Krishnapatnam than
Nelaturu 2.66±0.09. The levels of As observed nearly in Krishnapatnam
1.20±0.001 and in Nelaturu 1.16±0.02 was observed. However the concentrations
of Cu was 0.09±0.001 observed more than the permissible range at Krishnapatnam
coast and As, Pb, Cd, Cu were more than permissible levels and Fe and Zn were
observed within the ranges of IS 10500 and WHO water safety guidelines. Hg, Mn,
Cu, Zn were not observed at Nelaturu coast whereas, Hg and Mn were not observed
at Krishnapatnam coast. The concentrations of heavy metals obtained from AAS
analysis was presented in Table 1.
Table
1:
Heavy metals in the coastal water of
(Nelaturu, Krishnapatnam) Nellore (mg/lt) Mean±SD (n=6) in Andhra Pradesh, comparison with
WHO and IS: 10500 standards
S.No. |
Name of the Metal |
Nelaturu
COAST (Mean±SD) |
Krishnapatnam
Coast (Mean±SD) |
IS 10500 Standards |
W.H.O Standards |
1 |
Arsenic
(As) |
1.16±0.02 |
1.20±0.001 |
0.01 |
0.01 |
2 |
Lead
(Pb) |
4.67±0.12 |
3.64±0.02 |
0.01 |
0.01 |
3 |
Cadmium
(Cd) |
2.66±0.09 |
3.03±1.13 |
0.003 |
0.003 |
4 |
Mercury
(Hg) |
N.D |
N.D |
0.001 |
0.001 |
5 |
Iron
(Fe) |
0.04±0.004 |
0.01±0.0.001 |
0.3 |
0.2 |
6 |
Manganese
(Mn) |
N.D |
N.D |
0.1 |
0.5 |
7 |
Copper
(Cu) |
N.D |
0.09±0.001 |
0.05 |
2.0 |
8 |
Zinc
(Zn) |
N.D |
0.01±0.002 |
5.0 |
3.0 |
N.D=
Not Detected
DISCUSSION- The
ranges of the heavy metals were present in the coastal water of Nelaturu, Krishnapatnam
coastal regions of Nellore coast in the present study obtained from AAS
analysis was discussed below. Although there was no clear definition of what a
heavy metal density is in most cases taken to be the defining factor. Heavy
metals are thus generally defined as those having a specific density of more
than 5 g/cm3. Heavy metals are among the most common environmental
pollutants, and their occurrence in water and biota indicate the presence of
natural or anthropogenic sources. Although adverse health effects of heavy
metals have been known for a long time, discharge of heavy metals continues and
is even increasing in some areas are particular in less developed countries.
The main threats to human health from heavy metals are associated with exposure to lead, cadmium and mercury. Their
accumulation and distribution in soil, sediments and aquatic environment are
increasing at an alarming rate thereby affecting marine life [11-13].
A
number of elements are normally present in relatively low to high
concentrations, usually more than a few mg/L, in conventional irrigation water
and are called trace elements. Heavy metals are a special group of trace
elements which have been shown to create definite health hazards when taken up
by plants. The observed experimental value was very much higher than the
permissible limit of iron, which was 0.3 mg/L. The presence of high
concentration of Fe may increase the hazard of pathogenic organisms; since most
of these organisms need Fe for their growth [14].
Arsenic
(As) concentrations were observed 1.16 mg/L in Nelaturu beach, 1.20 mg/L in
Krishnapatnam coast. The maximum concentrations were observed in both study
areas. The permissible limit for Arsenic as per IS: 10500 is 0.01 mg/L and
maximum guideline value as per the WHO is 0.01 mg/L. However, the observed
concentration levels of Arsenic in the study area were observed as excess than
acceptable limits given by the IS: 10500 and WHO guidelines. Long-time exposure
to arsenic in drinking water can cause cancer in the skin, lungs, bladder, and
kidney. It can also cause other skin changes such as thickening and
pigmentation [15].
Lead
(Pb) concentrations were observed 4.67 mg/L in Nelaturu, 3.64 mg/L in
Krishnapatnam coast. The maximum concentrations were observed in both study
areas. The permissible limit for Lead is as per IS: 10500 is 0.01 mg/L. Lead is
a highly toxic metal substance, exposure to which can produce a wide range of
adverse health effects in both adults and children. Every year, industries
producing about 2.5 million tons of lead throughout the world that using for
making batteries. In adults, lead can increase blood pressure and cause
infertility problems, nerve disorders, muscle & joint pain, irritability
and memory or concentration problems come [16,18].
Cadmium
(Cd) concentrations were observed 2.66 mg/L in Nelaturu, 3.03 mg/L in
Krishnapatnam coast the maximum concentrations were observed in both study
areas. The permissible limit for Cadmium is as per IS: 10500 is 0.003 mg/L.
cadmium is widely distributed in the earth’s crust and is principally used in
many industries and in agriculture, according to USPH standards. Higher values
of Cd in waste water effluent samples suggest the high level of pollution due
to dyes paints and pigments manufacturing industries [14]. Cadmium
targets the liver, placenta, kidneys, lungs, brain, and bones. Consumption of
food or drinking water with very high cadmium levels severely irritates the
stomach, leading to vomiting and diarrhea and sometimes causes death [17].
Mercury
(Hg) concentrations were observed <1.0 mg/L below Detection Level (BDL) in
Nelaturu and Krishnapatnam coast. The maximum acceptable limit for Mercury as
per IS: 10500 is 0.001 mg/L permissible value and values are within the
permissible limits given by IS: 10500 and WHO guidelines. There are three forms
of mercury and among these the most toxic one is the organic form, viz., methyl
mercury. Methyl mercury is a microbiologically transformed form of inorganic
mercury when it reaches aquatic environments, water bodies or in soils.
Inorganic and organic mercury is toxic to the human body in different ways,
affecting different organs in different ways it may primarily expose to mercury
via food, where fish is the major source of methyl mercury exposure by biomagnification.
Mercury has no necessary function in any living organism and is considered as a
non-essential metal, and is among the most toxic elements to man and many
higher animals [19].
Iron
concentrations were observed 0.0487 mg/L in Nelaturu, 0.0107 mg/L in
Krishnapatnam coast. The maximum acceptable limit for iron as per IS: 10500 is
0.3 mg/L and no guideline value was given by the WHO for Iron content. However,
the observed concentration levels of Iron found within the permissible given by
the IS: 10500 CPCB [20].
Manganese (Mn) concentrations were
observed <1.0 mg/L BDL in Nelaturu and Krishnapatnam coast. The maximum
acceptable limit for Manganese as per IS: 10500 is 0.1 mg/L
and permissible value 0.3 mg/L and provisional guideline value as per the WHO
is 0.4 mg/L. The observed manganese values were within the permissible limits
given by IS: 10500 and WHO guidelines CPCB [20].
Copper
(Cu) concentrations were observed <1.0 mg/L BDL in Nelaturu, 0.096 mg/L in Krishnapatnam
coast. It is within the permissible limits at Nelaturu given by IS: 10500 and
WHO guidelines. Copper is one of the essential metals to life despite being as
inherently toxic as non-essential heavy metal exemplified by lead and mercury.
Plants and animals rapidly accumulate it. It is toxic at minute low concentration in water and is known to cause brain damage
in mammals. The natural inputs of copper to the marine aquatic environment are
from erosion of mineralized rocks or maybe from the industries. Anthropogenic
inputs of copper are from industries and paints. It also forms complexes with
organic molecules. Mollusks have a tremendous capacity to accumulate copper
from contaminated water CPCB [20].
Zinc (Zn) concentrations were observed <1.0 mg/L BDL in
Nelaturu, 0.01 mg/L in Krishnapatnam coast. It is within the permissible limits
at Nelaturu given by IS: 10500 and WHO guidelines. Zinc is an essential
nutrient for the human body and has importance for health also it acts as a
catalytic or structural component in many enzymes that are
involved in energy metabolism also. Symptoms of
zinc toxicity are slow reflexes, tremors, paralyzation of extremities, anemia,
metabolic disorder, teratogenicity effects and increased mortality in humans CPCB [20].
In the present seawater study the heavy metals of mercury, manganese and copper concentrations in the seawater have been observed in BDL<1.0 mg/L. Increased toxic heavy metal concentrations in the water lead to the Bioaccumulation factor in the aquatic food chain and its showed the transfer of metals especially arsenic, lead, cadmium, mercury are warning signal for fish consumption by humans towards food safety [20,21].
CONCLUSIONS- The environmental
parameters of water can be affected by the toxicity of the metal
either by influencing the physiology of organisms or by altering the chemical
form of the metal in water. The increased ambient heavy metal
concentration will result in accumulation in the tissues of commercially
important edible finfish, shellfish. It is an inherent danger of
higher bioaccumulation of toxins in the edible species that may
result in severe health hazards to the consumers especially human. It was evident
that the present study on heavy metals in the water of
the Nellore coast suggested adopting effective heavy metal removal
technologies to control the toxic metal contamination in coastal water.
Further bioaccumulation study to be
needed for better understanding the metal toxicity in the coastal and marine
environment.
ACKNOWLEDGEMENTS- Authors are thankful to
the Vimta Laboratories Pvt. Ltd. Nellore, for Atomic Absorption Spectroscopy
analysis.
CONTRIBUTION OF AUTHORS
Research concept- Dr. Ch. Venkatrayulu
Research design- Dr. Ch. Venkatrayulu
Supervision- Dr. Ch. Venkatrayulu
Materials- Mr. V. Venkateswarlu
Data collection- Mr. V. Venkateswarlu
Data analysis and Interpretation- Mr. V. Venkateswarlu
Literature search- Mr. V. Venkateswarlu
Writing article- Mr. V. Venkateswarlu
Critical review- Mr. V. Venkateswarlu
Article editing- Dr. Ch. Venkatrayulu
Final
approval- Dr. Ch. Venkatrayulu
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